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Property Details for Former Omaha Cold Storage


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Legal Notices

Profile Information

Private
151517
5025 S. 33rd St. Omaha, NE 68107
5.53
41.20754 / -95.960768
2
Morris, Jennifer
Morris.Jennifer@epa.gov
913-551-7341


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Property Location



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Property Progress


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CAs Associated with this Property

CA NameCA #StateTypeAnnouncement Year
Omaha-Council Bluffs Metro Area Planning AgencyBF97727901NEAssessment2011


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Assessment Activities at this Property

ActivityEPA FundingStart DateCompletion DateCAAccomplishment Counted?Counted When?
Cleanup Planning$10,000.0004/28/2014Omaha-Council Bluffs Metro Area Planning AgencyN
Phase I Environmental Assessment$13,000.0005/22/201208/30/2013Omaha-Council Bluffs Metro Area Planning AgencyYFY17
Phase II Environmental Assessment$12,000.0011/21/201304/23/2014Omaha-Council Bluffs Metro Area Planning AgencyN


Is Cleanup Necessary? Unknown
EPA Assessment Funding: $35,000.00
Leveraged Funding:
Total Funding: $35,000.00


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Climate Adaption and Mitigation - Planning or Assessment

There is no data for Climate Adaption and Mitigation - Planning or Assessment.


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Contaminants and Media


Asbestos
NOT Cleaned up
Building Materials
NOT Cleaned up


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Cleanup Activities

There are no current cleanup activities.


Cleanup/Treatment Implemented:
Cleanup/Treatement Categories:
Addl Cleanup/Treatment info:
Address of Data Source:
Total ACRES Cleaned Up: 5.53
Number of Cleanup Jobs Leveraged:
EPA Cleanup Funding:
Leveraged Funding:
Cost Share Funding:
Total Funding:


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Climate Adaption and Mitigation - Demolition or Cleanup

There is no data for Climate Adaption and Mitigation - Demolition or Cleanup.


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Institutional and Engineering Controls

No
No
No
No


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Redevelopment and Other Leveraged Accomplishments

There are no current redevelopment activities.


Number of Redevelopment Jobs Leveraged:
Actual Acreage of Greenspace Created:
Leveraged Funding:


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Climate Adaption and Mitigation - Redevelopment

There is no data for Climate Adaption and Mitigation – Redevelopment


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Additional Property Attributes

Concentrations of lead were below the residential RG. Therefore, observed lead concentrations in project site soils are not a significant concern with respect to property liability and/or constructability concerns with the redevelopment of the project site. Total extractable hydrocarbons (TEH) as gasoline, diesel, and waste oil diesel were detected in soil borings SB-4, SB-8, and SB-13. Note however that the NDEQ has not established residential or industrial standards for TEH in soils at VCP sites. In addition, the NDEQ standards for RBCA Tier I Site Assessments for petroleum sites in Nebraska do not include look up tables and values for TEH in soils at remedial action class three (RAC-3) sites, where there is no industrial or potable water use in the area. In summary, the presence of TEH in soils at B-4, B-8, and SB-13 are of generally insignificant concentrations, and not a significant concern with respect to property liability and/or constructability concerns with the redevelopment of the project site. Observed arsenic, barium, and lead concentrations in the groundwater were below the NDEQ RG for direct contact and the cadmium concentration that slightly exceeded the NDEQ RG is considered isolated and not widespread. Therefore, observed metal concentrations in project site's groundwater are not a significant concern with respect to property liability and/or constructability concerns with the redevelopment of the project site. Total extractable hydrocarbons (TEH) as gasoline and waste oil were detected in all of the groundwater sample (B-6, B-13, and B-16). Note however that the NDEQ has not established residential or industrial 10 direct contact or vapor intrusion (VI) standards for TEH in groundwater at VCP sites. In addition, the NDEQ standards for RBCA Tier I Site Assessments for petroleum sites in Nebraska do not include look up tables and values for TEH in groundwater at RAC-3 sites, where there is no industrial or potable water use in the area. In summary, the presence of TEH in groundwater at B-6, B-13, and B-16 is considered a generally minimal concentration and is not a significant concern with respect to property liability and/or constructability concerns with the redevelopment of the project site. Concentrations of VOC constituents in the soil vapor were considerably lower than the residential RGs. Therefore, observed VOC concentrations in project site soil vapors are not a significant concern with respect to property liability and/or constructability concerns with the redevelopment of the project site. Observed ACM in project structures is currently non-friable and in generally good condition, with the exception of the straight run piping insulation and pipe fitting insulation, and therefore, do not pose an immediate threat to human health. However, the friable materials are considered an immediate threat to human health, specifically the material that has fallen from the overhead piping runs onto the floor. It is recommended that prior to occupying the building, that the friable ACM be removed and disposed of according to Nebraska Asbestos Control Program Regulations and with proper notification provided to NDHHS and the City of Omaha. If the non-friable ACM materials will be disturbed during construction, renovation, or the structure demolition, such ACM should be removed and disposed of prior to such activities according to Nebraska Asbestos Control Program Regulations and with proper notification provided to NDHHS and the City of Omaha. LPB on the project structures will need to be abated if the site structures will be renovated. If the LBP abatement is required, it should be removed in accordance with NDHHS Title 178 Chapter 23. In addition, all workers interacting with and/or disturbing materials in the building should be notified of the presence of lead and its locations. With the exception of the ACM and LBP at the site as noted above, there are no concerns with respect to property liability and/or const
Industry (5.53)
Petroleum


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Release 3.0.1.2